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London Wider Waste Strategy - London - Greater London Authority

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R.38 It is recommended that consideration should be given in <strong>London</strong> to the way in which<br />

data on commercial and industrial waste arisings and the wastes handled – by customer<br />

type, customer size, and waste composition, could be obtained on a regular basis.<br />

R.39 It is recommended that consideration should be given to what extent the use of LPG<br />

and battery operated vehicles by waste collection authorities would be beneficial, and<br />

how such a change could be implemented.<br />

R.40 It is recommended that consideration should be given as to whether certain types of<br />

service provision by waste collection authorities are more advantageous than others,<br />

and, if so, how can additional support or information be given to such authorities in this<br />

regard.<br />

R.41 It is recommended that the GLA in conjunction with all <strong>London</strong> Boroughs should lobby<br />

Government to enable sufficient commercial waste facilities to be provided to handle<br />

<strong>London</strong>’s wider wastes (for example by adopting a similar approach to that of<br />

Copenhagen where the municipality has responsibility for the management of all<br />

commercial waste, including C&D waste, and sets criteria for the transport and<br />

treatment of each waste type; only those facilities and operations that meet the criteria<br />

can enter into a contract with the authorities to become designated waste management<br />

facilities and operators).<br />

R.42 In order to facilitate the provision of waste management facilities to serve <strong>London</strong>’s<br />

needs, it is recommended that suitable sites for a full range of facilities (ie. not just<br />

strategic facilities) are identified in <strong>Waste</strong> Local Plans in the light of consultation with<br />

the Regional Technical Advisory Board (RTAB).<br />

R.43 It is recommended an assessment is made of whether the use of environmental<br />

management systems (EMS) and quality management systems (QMS) by local<br />

authorities is likely to bring benefits with regard to sustainable waste management and,<br />

if so, to consider whether the provision of additional support to the authorities would be<br />

useful in this regard.<br />

Recommendations: Construction and Demolition <strong>Waste</strong>s<br />

R.44 It is recommended that the GLA make it clear that the arisings of ‘hard’ and excavated’<br />

construction and demolition wastes in <strong>London</strong> may be considerably different to the<br />

figure of 6.05 million tonnes that is often quoted from the Symonds’ surveys of 2001<br />

and 2002 and subsequently used as the basis for further analysis. Such analyses should<br />

recognise that the Symonds’ survey data should be used as a range (3.70-8.40 million<br />

tonnes), with the associated confidence level, and acknowledge the potential for<br />

significant uncertainty in the modelling results. An appropriate contingency should be<br />

included within any strategy measures based on the data modelling to allow for a<br />

significantly greater, or indeed lesser, quantity.<br />

R.45 It should be made clear that ‘soft’ C&D wastes (eg. timber, plastics, metals, packaging,<br />

plaster) are excluded from the Symonds’ survey data estimates, and future planning /<br />

modelling should take steps to (a) allow for this in any future waste modelling analyses,<br />

e.g. to inform the development of the <strong>London</strong> Plan, and (b) obtain data on the size and<br />

composition of this waste stream.<br />

R.46 It is recommended that the lack of reliable composition data is particularly taken into<br />

account in light of the level of uncertainty of the Symonds survey data estimates for<br />

<strong>London</strong>. Consideration should be given to commissioning a detailed survey of<br />

construction and demolition wastes in <strong>London</strong> that would include (a) the separate<br />

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